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® On August 16, 2007, at the request of Caltrans, the County performed a cursory investigation of <br /> the Caltrans property adjacent to the landfill. Refuse was found that was apparently consistent <br /> with normal household refuse placed during normal landfill operations. The refuse in Caltrans <br /> property was apparently placed prior to purchase by Caltrans while the City of Tracy operated <br /> the Corral Hollow Landfill. The County did not determine the full extent of refuse in the <br /> Caltrans property at that time. <br /> In a letter dated August 27, 2007, CDRRR staff directed the County and Caltrans to cover the <br /> refuse in both the Caltrans and County property according to Title 27 CCR in a common <br /> construction project. RWQCB staff reaffirmed this directive. However, Caltrans declined to <br /> participate, so the County submitted documents independently but awaited Caltrans' <br /> participation before proceeding with construction. <br /> In November 2007, an EMP was conducted, consisting of exploring for the presence of shallow <br /> aquifer groundwater along the northern and southern boundaries of the landfill. The purpose of <br /> this EMP was to extend the shallow aquifer monitoring program to the west to determine the <br /> extent of impact (if any) in that direction. Several boreholes were drilled along the boundary <br /> westward from existing well MW-5 on the north and from well MW-4 on the south. The <br /> investigation encountered a significant thickness to groundwater approximately 400 feet west of <br /> MW-5, where a new well MW-8 was installed. No shallow aquifer groundwater was detected <br /> further west than MW-8. On the southern boundary of the landfill, the exploration borings did <br /> not encounter shallow aquifer groundwater to the west of MW-4 and a new well was not <br /> installed on that side of the landfill. <br /> On January 14, 2008 (first monitoring event), VOCs were detected in monitoring of well -8. <br /> The compounds and concentrations detected indicate that the source of ground water <br /> contamination emanates from an area near MW-5, most likely from the refuse not well served by <br /> the existing LFG system near and extending across the property boundary. The County proposed <br /> to install three additional LFG wells in the area of this refuse to increase LFG capture. <br /> On April 1, 2008, the County submitted a revised Closure and Postclosure Maintenance Plan <br /> addressing the areas of the landfill known to contain refuse but that was not provided with a <br /> closure cap. The primary feature of this closure design was the use of geocomposite clay layer <br /> (GCL) overlain by one-foot vegetative layer. This design was accepted by RWQCB staff in a <br /> letter dated January 14, 2008 [sic]. <br /> On April 10, 2008, a new subsurface perimeter LFG migration monitoring well(GW-IA)was <br /> installed to replace well GW-1. Replacement was required because the deepest probe of the <br /> original GW-1 was found submerged,thereby preventing monitoring of offsite migration at that <br /> probe. Well GW-IA's installation allows monitoring through shallow, intermediate, and deep <br /> probes. <br /> In the Third Quarterly Report of 2008,the increase in alkalinity in MW-4 and—5 above the <br /> established concentration limits was noted. However, in the third quarter 2010,this condition <br /> was seen only at SB-l. <br /> • <br /> Corral Hollow Sanitary Landfill 4 Department of Public Works/Solid Waste <br /> 3`"Quarter 2012 Groundwater Monitoring County of San Joaquin—October 30,2012 <br />